Nebulizing treatment method

ABSTRACT

A method of treating contaminated air, gas and surfaces is accomplished through the nebulization of gas and/or liquid oxidants through a field of electromagnetic radiation or sonic waves. The contaminated gas and/or liquid streams are blended with gaseous and/or liquid oxidants by the nebulizer and directly injected in the energy field. Free radicals produced from oxidants in the presence of the energy field instantaneously oxidize a large effective surface area of the contaminated media. Surfaces are treated more efficiently with the energy field situated directly above and parallel to but not on the surface; a high-frequency energy field may be used to create a large concentration of free radicals without damaging the surface in a collimated beam of the field situated parallel to the surface. A catalyst may be employed at the tip (i.e. discharge orifices of gas and/or liquid) of the nebulizer or blended into the nebulized cloud to increase the formation of free radicals. The method may also be used to carry out a reduction instead of an oxidation reaction.

CROSS-REFERENCE TO RELATED APPLICATIONS

Priority of U.S. Provisional Patent Application Ser. No. 60/631,781, filed 30 Nov. 2004, incorporated herein by reference, is hereby claimed.

STATEMENT REGARDING FEDERALLY SPONSORED RESEARCH OR DEVELOPMENT

Not applicable

REFERENCE TO A “MICROFICHE APPENDIX”

Not applicable

BACKGROUND OF THE INVENTION

1. Field of the Invention

This invention relates to a method of oxidatively treating gases, liquids, slurries and surfaces in which high energy oxidants are created through the nebulization of an oxidizer into an energy field. If the media requiring treatment may itself be nebulized, treatment will occur within the radiation/energy field. If the media requiring treatment is a surface or bulk slurry, the energy field is positioned directly above but not on the surface requiring treatment. This oxidation method may be employed for disinfection, purification, sterilization, destruction of organic molecules, oxidation of inorganics, oxidation of metals, and co-precipitation of metals.

2. General Background of the Invention

Free radical formation is a process that has been developed for the purification and disinfection of contaminated liquids, gases, and surfaces. The present invention is an efficient method of free radical application through instantaneous formation of free radicals through the nebulization of liquid and gas oxidants through an energy field.

The process of nebulization or atomization has per se been used in prior art for the dispersion of powders or liquids into clouds (U.S. Pat. No. 4,993,411), humidification of air or oxygen gas for inhalation (U.S. Pat. Nos. 6,511,050; 5,407,604; 4,993,411) the dispersion of fuel into a cloud for efficient combustion (U.S. Pat. Nos. 4,696,719; 4,267,976), and the saturation of a liquid with oxygen, ozone or other gas (U.S. Pat. No. 5,366,696). The dispersion of liquids, slurries or solids into nano-sized droplets or particles increases the effective surface area available for instantaneous reaction and therefore increases efficiency of processes.

Prior art nebulizers which can be used in this process include two examples shown in U.S. Pat. Nos. 4,344,574 (cross-flow) and 4,575,605 (concentric), which both atomize a liquid with a gas at high velocity.

Concentric nebulizers have evolved into models with adjustable inner capillary tubes (see for example U.S. Pat. No. 5,884,846), tips with varying geometry (see for example U.S. Pat. No. 6,032,876), direct injection high efficiency models (see for example U.S. Pat. No. 6,166,379), a supersonic nozzle nebulization apparatus (see for example U.S. Pat. No. 6,009,869), a concentric nebulizer with electrospray capability (see for example U.S. Pat. Nos. 6,478,238 and 6,126,086), and a model with parallel paths of gas (surrounding the liquid capillary) with different velocities to direct the cloud of liquid droplets in a specific direction. A combined cross-flow ultrasonic nebulizer has also been developed (see for example U.S. Pat. No. 4,961,885.)

Other apparatuses and methods for nebulizing or atomizing a liquid solution with gas have been patented including a method of thermal pressurization (U.S. Pat. No. 6,601,776), ultrasonication (U.S. Pat. Nos. 6,555,011; 5,922,247), centrifugal pressurization (U.S. Pat. No. 5,727,541) and specialty nozzles (U.S. Pat. No. 5,269,461). These prior art references support the claimed method when the atomized liquid is combined with a stream of gas moving at substantial velocity.

Prior art patents also include any process which combines an energy field and an oxidant for the treatment of gases, liquids and solids in bulk (see U.S. Pat. Nos. 6,761,863; 6,761,729; 6,555,835; 6,468,433; 6,264,899; 5,765,403; 5,688,378; 4,816,145; 4,265,747); of particular application are advanced oxidation processes which generate hydroxyl radicals (OH.) for oxidative treatment of media (see U.S. Pat. Nos. 6,780,306; 6,630,105; 6,361,697; 6,328,898; 6,264,899; 6,200,466; 6,030,526; 5,512,244; 5,364,537; 5,213,759; 4,849,114).

Liquid treatment systems include compounded reactors geometrically shaped to enhance internally applied UV energy (see U.S. Pat. No. 6,555,011); mixing oxygen, ozone and or hydrogen peroxide into the liquid and contacting the mixture with a free radical inducer (see U.S. Pat. No. 6,361,697); pulse-discharge treatment of oxygen saturated liquid (see U.S. Pat. No. 6,328,898); treatment of water with blackbody radiation (see U.S. Pat. No. 6,200,466); dual annular UV reactor which respectively form ozone from dissolved oxygen and then initiate free radical formation with photolysis of titanium dioxide (see U.S. Pat. No. 6,030,526); dissolution of UV treated humid air, referred to as active air (containing only peroxide and hydroxyl radicals) into a liquid (see U.S. Pat. No. 5,765,403); dissolved oxygen and or photoabsorbers (metals/cations) are irradiated in the liquid being treated; combining ozone and hydrogen peroxide in water to create free radicals (U.S. Pat. No. 5,634,537); dissolved ozone and hydrogen peroxide irradiated with UV light (U.S. Pat. No. 4,849,114); laser disinfection of fluids (U.S. Pat. Nos. 4,816,145; 4,265,747)

Surface decontamination systems include a wand which sprays (using a nozzle) ozone combined with water vapor and hydrogen peroxide onto surfaces which are irradiated by a UV source (either a lamp or a fiber optic cable) on the tip of the wand (see U.S. Pat. No. 6,630,105); a reaction chamber in which the thing being treated is heated on a sample stage while being irradiated from above with a UV lamp in a ozone atmosphere; sterilization of an object by exposing it to an activated gas medium, composed of irradiated SF₆, H₂O, O₂, H₂S, CO, C₂H₂, Hg, NO, Cl₂, N₂O, C₂H₆ or mixtures thereof. (U.S. Pat. No. 5,512,244); ultrasonic nebulization of antiseptic solution (U.S. Pat. No. 5,449,502); and wound treatment with ultrasonic atomization of liquid and laser light (U.S. Pat. No. 6,761,729). A spray device which is based on ICP-MS nebulizer technology also exists for the misting of surfaces with various liquids and gases (U.S. Pat. No. 6,848,633).

Gas purification systems include a method of removing pollutants from flue gas by ozonation of the gas, followed by wet scrubbing, followed by ultra-violet radiation (see U.S. Pat. No. 6,761,863); in this invention, NO_(x), SO_(x), and Hg are oxidized by ozone and UV radiation to water soluble species which are removed from the gas phase into the liquid phase. The concentric nebulization of ozone with water is also patent pending for the disinfection of surfaces and treatment of gaseous odors (2004/0096354 A1). Pressurization systems in prior art allow for greater mass transfer of gas into liquids (see U.S. Pat. No. 5,971,368).

Prior art also involves catalysts which can be employed for photolytic production of hydroxyl radicals (see U.S. Pat. No. 6,866,755) include titanium dioxide (TiO₂), tungsten oxide (WO₃), zinc oxide (ZnO) and other semiconductor catalysts which produce electron hole pairs when irradiated with ultraviolet or ionizing energy; catalysts which generally speed up reaction rates are also applicable.

The method of treatment of media with nebulized oxidant combined with a radiation or energy field and catalyst is unique to the present invention. This new method is designed for superior treatment efficiency due to increased surface area for reaction between oxidants, radiation and constituent requiring oxidation leading to overall more rapid treatment time; it is also a convenient method of generating reactive oxidants for immediate application to a surface without damaging or weakening the surface with direct application of radiation or energy.

The following above-discussed US patents are listed in the following table, each patent hereby incorporated herein by reference: TABLE PATENT NO. TITLE ISSUE DATE 4,265,747 Disinfection and purification May 19, 1981 of fluids using focused laser radiation 4,267,976 Apparatus for vaporizing and May 19, 1981 atomizing liquids 4,344,574 Cross-flow nebulizer Aug. 17, 1981 4,575,609 Concentric micro-nebulizer for Mar. 11, direct sample insertion 1986 4,696,719 Monomer atomizer for Sept. 29, vaporization 1987 4,816,145 Laser disinfection of fluids Mar. 28, 1989 4,849,114 Oxidation of toxic compounds Jul. 18, in water 1989 4,961,885 Ultrasonic nebulizer Oct. 9, 1990 4,993,411 Ultrasonic oxygen humidifier Feb. 19, 1991 5,213,759 Sterilization May 25, 1993 5,269,461 Aerosol nozzle system Dec. 14, 1993 5,364,537 Process for the oxidation of Nov. 15, organic micropollutants in 1994 water using the O.sub.3/ H.sub.2 O.sub.2 combination 5,366,696 Oxygenation apparatus for Nov. 22, oxygenating a carrier liquid by 1994 spraying 5,407,604 Humidifier using a neubilizer Apr. 18, 1995 5,449,502 Sterilizing apparatus Sept. 12, utilizing ultrasonic vibration 1995 5,512,244 Gas sterilization Apr. 30, 1996 5,688,378 Photoassisted oxidation of Nov. 18, species in solution 1997 5,727,541 Atomization of liquids Mar. 17, 1998 5,765,403 Water treatment method and Jun. 16, apparatus 1998 5,884,846 Pneumatic concentric nebulizer Mar. 23, with adjustable and 1999 capillaries 5,922,247 Ultrasonic device for Jul. 13, atomizing liquids 1999 5,971,368 System to increase the quantity Oct. 26, of dissolved gas in a liquid 1999 and to maintain the increased quantity of dissolved gas in the liquid until utilized 6,009,869 Supersonic nozzle nebulizer Jan. 4, 2000 6,032,876 Apparatus for forming liquid Mar. 7, droplets having a mechanically 2000 fixed inner microtube 6,030,526 Water treatment and Feb. 29, purification 2000 6,126,486 Oscillating capillary Oct. 3, 2000 nebulizer with electrospray 6,166,379 Direct injection high Dec. 26, efficiency nebulizer for 2000 analytical spectrometry 6,200,466 Decontamination of water by Mar. 13, photolytic oxidation/reduction 2001 utilizing near blackbody radiation 6,264,899 Method and apparatus for using Jul. 24, hydroxyl to reduce pollutants 2001 in the exhaust gases from the combustion of a fuel 6,328,898 Method of and apparatus for Dec. 11, forming highly oxidative water 2001 6,361,697 Decontamination reactor system Mar. 26, and method of using same 2002 6,468,433 Method for disinfecting liquids Oct. 22, and gases and devices for use 2002 thereof 6,478,238 Miniaturized fluid transfer Nov. 12, device 2002 6,511,050 Humidifier Jan. 28, 2003 6,555,011 Method for disinfecting and Apr. 29, purifying liquids and gasses 2003 6,555,835 Ultraviolet-ozone oxidation Apr. 29, system and method 2003 6,630,105 Method and apparatus for the Oct. 7, 2003 gas phase decontamination of chemical and biological agents 6,601,776 Liquid atomization methods and Aug. 5, 2003 devices 6,761,729 Wound treatment method and Jul. 13, device with combination of 2004 ultrasound and laser energy 6,761,863 Process for the removal of Jul. 13, impurities from gas streams 2004 6,780,306 Electrionic water disinfection Aug. 24, apparatus 2004 6,848,633 Spray device Feb. 1, 2005 6,866,755 Photolytic artificial lung Mar. 15, 2005 20040096354 Ozone deodorizing and May 20, 2004 sterilizing method and device EP0430904 Process for treating waste Nov. 9, 1990 water with high concentration ozone water

BRIEF SUMMARY OF THE INVENTION

The method of the present invention involves combining an oxidant into a liquid solution or gas through nebulization or atomization. This dispersion process also promotes interaction of the gaseous and liquid molecules which promotes oxidation reactions. The oxidant may itself be a liquid or a gas. When the oxidant is a liquid, it can be delivered undiluted or combined with a solvent or combined with the liquid to be treated. When the oxidant is a gas, it is used by itself or can be combined with the gas to be treated as the carrier gas for nebulization or atomization. As used herein, nebulizing and atomizing are interchangeable, each being defined as a process that includes the mechanical, electrical (e.g. electrospray, see http://www.newoblective.com/electrospray/index.html) or ultrasonic subdivision of a liquid to produce drops or droplets. The oxidant gas or oxidant/polluted gas mixture may then be nebulized with a liquid into the radiation field.

Ultraviolet or ionizing radiation is used to initiate reactions which form highly reactive oxidant species, such as free radicals (OH.); the radiation itself will also decompose some organic species (dependent on bond dissociation energies) but the combination of radiation and chemical oxidation as an advanced oxidation process will decompose all organics as well as oxidize metals and kill microorganisms. The frequency of energy used must be chosen based on the absorption requirements of the employed oxidant. For example, ozone is effectively decomposed into singlet oxygen by electromagnetic radiation with a wavelength less than approximately 300 nm and water is decomposed into hydroxyl radicals at a wavelength less than approximately 190 nm. Gamma rays (wavelengths less than approximately 0.1 nm) are already present when waste being treated is radioactive so the natural energy source within the waste may be incorporated into the design. All gamma radiation induces hydroxyl radical formation in water and also decomposes organics. Sonic energy induces hydroxyl radical formation through cavitation.

BRIEF DESCRIPTION OF THE SEVERAL VIEWS OF THE DRAWINGS

For a further understanding of the nature, objects, and advantages of the present invention, reference should be had to the following detailed description, read in conjunction with the following drawings, wherein like reference numerals denote like elements and wherein:

FIG. 1 is a partial perspective view of the preferred embodiment of the apparatus of the present invention illustrating the nebulizer portion thereof and the method with the distal outlet of the nebulizer is inserted into the energy field;

FIG. 2 is a schematic diagram of the preferred embodiment of the apparatus of the present invention and of the method showing a nebulized cloud injected through an energy field onto a surface;

FIG. 3 is a graphical representation of the treatment of EDTA solution by nebulized hydrogen peroxide and/or ozone;

FIG. 4 is a graphical representation of the treatment of EDTA solution by nebulized hydrogen peroxide and/or ozone; and

FIG. 5 is a graphical representation showing the oxidation of CR(III) to CR(VI) by nebulized ozone in a UV radiation field.

DETAILED DESCRIPTION OF THE INVENTION

An example of a nebulizer 10 which can be used to combine liquid and gas is shown in FIG. 1. This device 10 can be a commercially available concentric nebulizer. The types of nebulizers which can be employed in the present invention are not limited to that pictured in FIG. 1, but can be any kind of nebulizer which atomizes a liquid through the action of a carrier gas, an applied voltage or ultrasonic waves.

Nebulizer 10 provides a pair of inlets 1, 2. Inlet 1 is a flow inlet that is used to introduce a liquid to be nebulized. The inlet 2 is an inlet for introducing a carrier gas. A liquid discharge orifice 3 and a gas discharge orifice 9 is provided at distal end portion 13 of nebulizer 10 opposite the flow inlets 1, 2 as shown in FIG. 1. During use, the nebulizer 10 uses a carrier gas injected at inlet 1 transmitted via conduit 5 to orifice 9. The liquid to be nebulized is introduced at inlet 2 and travels through conduit 6 until it reaches orifice 9. The conduits 5, 6 can be concentric as shown in FIG. 1. The orifices 3, 9 can also be concentric.

A nebulized cloud 4 is discharged as indicated by arrow 8 in FIG. 1. The nebulized cloud 4 can be injected through an energy field 11 onto a surface 12, as shown in FIG. 2.

The treatment of EDTA solution by nebulized hydrogen peroxide and or ozone in a 254 nm or combined 185/254 nm UV radiation field is shown in FIGS. 3 and 4.

The oxidation of Cr(III) to Cr(VI) by nebulized ozone in a 254 nm UV radiation field is shown in FIG. 5.

FIG. 3 shows degradation of EDTA in screening experiments to test the effectiveness of nebulized O₃, O₂, H₂O₂ and different UV lamps in plug flow and batch treatment. Experimental conditions: [EDTA]_(i)=200 or 400 mg/L, pH uncontrolled (pH=5.77±0.6), T=20.6±0.5° C.

FIG. 4 shows a comparison of nebulized O₃, nebulized O₃+254 nm UV, and nebulized H₂O₂+254 nm UV oxidation of EDTA during recirculating batch experiments. Experimental conditions: [EDTA]_(i)˜210 mg/L, pH uncontrolled (pH=7.1±0.6), T=21.2±1.9° C.

FIG. 5 shows milliequivalents of electrons transferred during oxidation of Cr(III). Experimental Conditions: [Cr³⁺]=90 mg/L for all except α, where [Cr³⁺]=10 mg/L), pH uncontrolled (pH=3.96±0.53), T=22.3±1.5° C.

The embodiments of the present invention described below are not intended to be exhaustive or to limit the invention to the precise forms disclosed in the following detailed description. Rather the embodiments are chosen and described so that others skilled in the art may appreciate and understand the principles and practices of the present invention.

EXAMPLE 1

This example illustrates the mechanism by which a liquid is treated. The liquid requiring treatment may be blended with another liquid (a solvent or oxidant chosen based on the application of the method) and is pumped through the inner capillary tube through the liquid inlet 1 of the nebulizer. A carrier gas, which may also be an oxidant, is routed through the gas inlet 2 of the nebulizer. The liquid requiring treatment is atomized into small droplets by the carrier gas at the tip of the nebulizer 3. The liquid droplets and gas are injected into an energy field 4; the tip of the nebulizer may also be coated with a photocatalyst which, when inserted into a ultraviolet or ionizing radiation field will promote oxidation reactions. The liquid and/or gas oxidant as well as any nanoparticulate photocatalyst added to the liquid or gas will be energized by the field to form excited species, such as free radicals, which are more powerful oxidants than the parent compound. Gas oxidants will oxidize the contaminants in the liquid at the surface of the droplets and liquid oxidants will oxidize the contaminants inside the droplets. Dose of the oxidants must be designed based on the concentration of contaminant.

Examples of gaseous oxidants which may be used as parent compounds to form reactive gas or dissolved species include but are not limited to:

-   -   1. Ozone (O₃) which forms singlet oxygen O¹D upon excitation     -   2. Nitrogen Dioxide, NO₂, which dissolves into water as nitric         acid HNO₃ and becomes peroxynitrous acid (HONOO) upon         excitation.

Examples of liquid oxidants which may be used as parent compounds to form reactive dissolved species include but are not limited to:

-   -   1. Hydrogen peroxide (H₂O₂) which splits into 2 hydroxyl         radicals (OH.) upon excitation     -   2. Persulfate (S₂O₈) which forms sulfate radicals (SO₃ ⁻.) upon         excitation

Examples of catalysts which may be used to promote oxidation reactions include but are not limited to:

1. Titanium dioxide (TiO₂)

2. Tunsten oxide (WO₃)

3. Zinc Oxide (ZnO)

4. Tantalum and Nickel Oxides Cocatalyst

Examples of the energy field which may be used to promote reactive species formation include but are not limited to:

1. Ultraviolet radiation (UV)

2. Sonication

3. X-Rays

4. Gamma Rays

5. Microwaves

EXAMPLE 2

This example illustrates the mechanism by which a contaminated gas is treated. The gas requiring treatment may be blended with another gas before being routed through the gas inlet 2 of the nebulizer. A liquid solvent and/or oxidant, chosen based on the application of the method, is pumped through the inner capillary tube through the liquid inlet 1 of the nebulizer. Liquid droplets are formed from the velocity of the gas at the tip of the nebulizer 3 and both are injected into the energy field 4. Particulates and volatile organic or inorganic species in the gas requiring treatment may be scrubbed in the nebulized liquid droplets before or after oxidation to soluble species. Oxidation may occur in the gas phase by the direct action of the energy field, or by excited species formed in the gas, or may occur in the liquid phase. Gaseous organic species may also be mineralized to carbon dioxide (CO₂) by oxidants at the surface of the liquid. Dose of the oxidants can be designed based on the concentration of contaminant.

The examples of gas and liquid oxidants as well as energy fields and catalysts described in Example 1 are also applicable in this example.

This embodiment can be specifically employed in devices for the purification and decontamination of air in rooms or within ventilation systems.

EXAMPLE 3

A gas and liquid are simultaneously treated. The combined methods described in examples 1 and 2 are simultaneously employed to treat a contaminated gas and a contaminated liquid.

This embodiment can be specifically employed in a compact device for the simultaneous treatment of drinking water and indoor air.

EXAMPLE 4

A surface 12 is treated by the nebulized excited mist/cloud 11. A liquid oxidant and/or solvent is pumped through the inner capillary tube or conduit 5 via liquid inlet 1 of the nebulizer 10 (see arrow 14). A carrier gas, which may also be an oxidant, is routed through the gas inlet 2 of the nebulizer 10 (see arrow 15). The liquid is atomized into small droplets 7 by the carrier gas at the distal tip 13 of the nebulizer 10 and are injected with the gas into an energy field 11. The energy field 11 can be produced from a collimating source 16 so that the energy field 11 is parallel to but not touching the surface 8.

The following is a list of parts and materials suitable for use in the present invention.

PARTS LIST

Part Number Description

-   -   1 liquid inlet     -   2 gas inlet     -   3 liquid outlet orifice     -   4 nebulized cloud     -   5 capillary tube/liquid conduit     -   6 gas conduit     -   7 droplet     -   8 arrow     -   9 gas outlet orifice     -   10 nebulizer     -   11 energy field     -   12 surface     -   13 distal tip     -   14 arrow     -   15 arrow

All measurements disclosed herein are at standard temperature and pressure, at sea level on Earth, unless indicated otherwise. All materials used or intended to be used in a human being are biocompatible, unless indicated otherwise.

The foregoing embodiments are presented by way of example only; the scope of the present invention is to be limited only by the following claims. 

1-8. (canceled)
 9. A method of treating a waste water stream comprising the steps of: a) providing a nebulizer having a liquid inlet and a gas inlet that each communicate with an outlet; b) transmitting an influent waste water flow stream to the liquid inlet; c)transmitting an influent carrier gas stream to the gas inlet; d) using the gas stream to atomize the fluid that is emitted by the orifice, forming small droplets downstream of the orifice; and e) treating the atomized fluid of step “d” with a radiation field.
 10. The method of treating a waste water stream of claim 9 wherein in step “e” the radiation field is an ultraviolet radiation field.
 11. The method of treating a waste water stream of claim 9 wherein in step “e” the radiation field is an X-ray radiation field.
 12. The method of treating a waste water stream of claim 9 wherein in step “e” the radiation field is a gamma ray radiation field.
 13. The method of treating a waste water stream of claim 9 wherein in step “e” the radiation field is a sonic energy radiation field.
 14. The method of claim 9 further comprising the step of mixing the waste water stream with an oxidant.
 15. The method of claim 14 further comprising the step of mixing the waste water stream with an oxidant before step “b”.
 16. The method of claim 14 wherein the oxidant is hydrogen peroxide.
 17. The method of claim 15 wherein the oxidant is hydrogen peroxide.
 18. The method of claim 15 wherein any liquid that is an oxidant or may form oxidants upon exposure to the radiation field is used.
 19. The method of claim 9 wherein step “c” includes transmitting a gas stream that includes oxygen.
 20. The method of claim 9 wherein step “c” includes transmitting a gas stream that includes ozone.
 21. The method of claim 9 wherein step “c” includes transmitting a gas stream that includes any gas that is an oxidant or may form excited species upon exposure to the radiation field.
 22. The method of claim 9 wherein step “c” includes transmitting a gas stream that includes any gas that dissolves into the chosen solvent to form an oxidant prior to or upon exposure to the radiation field.
 23. The method of claim 9 wherein oxidation reduction reactions take place on the surface of the droplets in steps “d” and “e”.
 24. The method of claim 9 wherein the waste water stream in step “a” includes organic matter.
 25. The method of claim 9 wherein the waste water stream in step “a” includes dissolved, colloidal, particulate metals or inorganic species.
 26. The method of claim 9 wherein the atomized fluid contains an ozone and waste water vapor.
 27. The method of claim 9 wherein the cross section of the orifice is smaller than the cross section of the gas inlet.
 28. The method of claim 9 further comprising pressurizing the gas inlet stream in step “c”.
 29. The method of claim 9 wherein the cross sectional area of the fluid outlet is smaller than the cross sectional area of the inlet orifices to create a pressurized stream of gas and a fine flow of liquid combined to produce a spray of ultra-fine droplets.
 30. A method of treating a waste stream comprising the steps of: a) providing a nebulizer having a liquid inlet, a gas inlet, and an outlet for emitting atomized fluid; b) transmitting a liquid stream to the liquid inlet; c)transmitting a gas stream to the gas inlet; d) using the gas stream and/or an applied viltage and/or ultrasonic waves to break up the liquid stream into droplets; e) discharging the droplets and gas from the outlet as an atomized fluid mixture; f) irradiating the atomized fluid mixture; and g) wherein in steps “e” and “f” the atomized fluid mixture includes a waste material to be treated; and h) wherein the waste material is treated with irradiation in step “f”.
 31. The method of claim 30 wherein the waste material includes liquid waste material.
 32. The method of claim 30 wherein the waste material includes gaseous waste material.
 33. The method of claim 30 wherein the waste material includes slurried waste material.
 34. The method of claim 30 wherein the atomized material includes a media having at least one of a gas, liquid or particle that is to be treated.
 35. The method of claim 30 wherein step “e” includes producing micro sized droplets.
 36. The method of claim 30 wherein step “e” included producing nano sized droplets.
 37. The method of claim 30 wherein step “e” included producing micro sized particles.
 38. The method of claim 30 wherein step “e” included producing nano sized particles.
 39. The method of claim 30 wherein step “f” includes irradiating the mixture with a field of electromagnetic or sonic energy.
 40. The method of claim 39 wherein the field of electromagnetic energy is of a wavelength that enables formation of a high energy reactive oxidizing species.
 41. The method of claim 40 wherein the high energy reactive species includes free radicals.
 42. The method of claim 30 further comprising the step of adjusting temperature within the nebulizer.
 43. The method of claim 30 further comprising the step of adjusting pressure within the nebulizer.
 44. The method of claim 42 wherein the temperature range is between a lower limit under which chemical reactions will not proceed and an upper limit past which materials of construction will be destroyed.
 45. The method of claim 30 further comprising the step of adding nanoparticles of a catalyst to the atomized mixture.
 46. The method of claim 30 further comprising the step of adding nanoparticles of a catalyst to the atomized mixture to enhance reactive species production.
 47. The method of claim 30 further comprising the step of adding nanoparticles of a catalyst to the atomized mixture to enhance hydroxyl radical production.
 48. The method of claim 30 further comprising the step of adding a catalyst to at least part of the surface of the nebulizer to enhance reactive species production.
 49. The method of claim 30 further comprising the step of adding a catalyst to at least part of the surface of the nebulizer to enhance hydroxyl radical production.
 50. The method of claim 49 wherein the catalyst is added to the surface of the nebulizer next to the outlet.
 51. The method of claim 50 further comprising the step of adding a catalyst to at least part of the surface of the nebulizer to enhance hydroxyl radical production.
 52. A method of treating a waste stream comprising the steps of: a) providing a nebulizer having a liquid inlet, a gas inlet, and an outlet for emitting atomized fluid; b)transmitting a liquid stream to the liquid inlet; c) transmitting a gas stream to the gas inlet; d) using the gas stream to break up the liquid stream into droplets; e) discharging the droplets from the outlet as an atomized fluid mixture, wherein the droplets include an oxidant; f) treating the atomized fluid mixture with a field of radiation or energy; and g) wherein the atomized fluid mixture is immediately applied after step “f” to a media that requires treatment.
 53. The method of claim 52 wherein the media is a surface.
 54. The method of claim 53 wherein the media is a slurry.
 55. The method of claim 52 wherein the gas stream is pressurized.
 56. The method of claim 52 wherein the outlet is sized and shaped to produce nanodroplets.
 57. The method of claim 52 wherein the outlet has a diameter on the order of millimeters in order to produce nanodroplets.
 58. The method of claim 9 in which a constituent is reduced instead of oxidized.
 59. A method of treating a waste stream comprising the steps of: a) providing a liquid stream that includes a waste material to be treated; b) breaking up the liquid stream into droplets; c) irradiating the droplets; and d) wherein the waste material is treated with irradiation in step “c”.
 60. The method of claim 59 wherein the liquid stream is mechanically broken up into droplets in step “b”.
 61. The method of claim 59 wherein the liquid stream is broken up with an applied voltage.
 62. The method of claim 59 wherein the liquid stream is broken up with ultrasonic waves.
 63. The method of claim 59 wherein the liquid stream is broken into droplets with a combination of mechanical forces, applied voltage or ultrasonic waves.
 64. (canceled) 